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USDA-ARS, Forage and Range Research Laboratory, Utah State Univ., Logan, UT 84322-6300
Corresponding author (khasay{at}cc.usu.edu)
| ABSTRACT |
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1.0) for most cultivars later in the season. Differences in DMY between Ky 31 tall fescue infected with the Neotyphodium endophyte and its endophyte-free counterpart confirms earlier reports of the positive effect of this fungal organism on forage yield in tall fescue, particularly in water-limited environments. Seasonal distribution of yield was primarily determined by water availability during the late summer and fall. The relative consistency in DMY of the cultivars across WL indicates that annual yield averaged across levels of water stress would be a logical criterion for selection of germplasm for irrigated pastures in the Intermountain Region. | INTRODUCTION |
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Tall fescue was introduced from Europe in the mid-1800s. Following its rapid expansion during the 1940s through the 1960s, it became the predominant cool-season perennial grass in the USA. It is particularly popular in the transition zone between the adaptative areas of cool-season and warm-season grasses (Sleper and West, 1996). Much of the popularity of tall fescue can be attributed to its adaptation to a wide range of soil, climatic, and management conditions.
Tall fescue is a hexaploid (2n = 6x = 42) and cross-fertilizing grass. Early breeding programs were based on isolation of selected accessions or naturalized populations. The release of two cultivarsKy 31 and Altawere instrumental in the early expansion of the species (Buckner et al., 1979; Cowan, 1956). Subsequent breeding programs in the public and private sectors have emphasized recurrent selection involving the application of various forms of progeny testing (Asay et al., 1979; Sleper, 1985; Sleper and West, 1996), and several forage and turf cultivars have since been released (Alderson and Sharp, 1994).
Animals grazing or fed tall fescue may suffer from a number of disorders including fescue foot, fat necrosis, and fescue toxicosis (Schmidt and Osborn, 1993), and there is evidence that the alkaloid ergovaline is responsible for many of these disorders (Stuedemann and Thompson, 1993). An endophyte, classified as Neotyphodium coenophialum (Morgan-Jones & Gems) Glenn, Bacon & Hanlin has been identified with the fescue toxicity syndrome (Bacon et al., 1977; Bacon, 1995). The detrimental effects of the endophyte on the grazing animal have been confirmed in several studies including those by Hoveland et al. (1983). Shelby and Dalrymple, (1987) estimated that 90% of the tall fescue pastures in the USA were infested to some degree with the endophyte. Beef losses attributed to this fungus in tall fescue forage exceed more than $600 million annually (Hoveland, 1993).
The presence of the endophyte has now been associated with many of the positive attributes of tall fescue, including its wide adaptation and tolerance of biotic and abiotic stress (West and Gwinn, 1993). Tall fescue infected with the endophyte is reported to be more persistent than endophyte-free types in heat-stressed environments such as the Ozarks (West et al., 1988), Coastal Plains (Joost and Coombs, 1988), and the southern Piedmont (Hill et al., 1991). Procedures involved in breeding endophyte-free cultivars are discussed by Pedersen and Sleper (1988), and several endophyte-free cultivars of tall fescue have now been released. Progress has been made to develop forage-type cultivars containing endophytes that contribute to drought and pest resistance but have little or no toxic effects on the grazing animal (West et al., 1998).
Water for irrigation is limited in much of the West, particularly during the late summer. Cultivars developed for this region must, therefore, maintain an adequate level of production during periods of drought and be able to respond to more favorable conditions when water becomes available. If progress is to be made in breeding tall fescue cultivars that are better adapted to these environmental conditions, an understanding of the genetic responses to varying degrees of water stress must be obtained.
A line-source sprinkler system has been used to control the amount of water applied to an experimental area (Hanks et al., 1976.). The system was modified for use in the greenhouse (Johnson et al., 1982), and the procedure was used in the greenhouse and field to evaluate the intraspecific responses of alfalfa (Medicago sativa L.) and the RS wheatgrass hybrid (Elymus hoffmanni Jensen & Asay) to different levels of water stress (Rumbaugh et al., 1984). The line-source irrigation system also was employed by Asay and Johnson (1990) in a rain-out shelter to determine the genetic variability among crested wheatgrass [Agropyron desertorum (Fisch. Ex Link) Schultes] progeny lines at six levels of water application.
Certain limitations must be recognized in the statistical analyses and interpretation of data from experiments obtained with the line-source irrigation system (Hanks et al., 1980). Because water levels are not imposed randomly for each plot within a replication, a valid error term is not available for testing the main effects for water levels. An error term is available for testing the effects of other treatments and their interactions with water levels, providing the treatments (cultivars, species, etc.) are randomized within replications.
Objectives were to study (i) the trends and stability in forage yield across water levels, (ii) the effect of water level on seasonal distribution of forage yield, and (iii) effects of the Neotyphodium endophyte on productivity and trends.
| MATERIALS AND METHODS |
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The experimental plots were established at the Utah State University Evans Research Farm, approximately 2 km south of Logan, UT (41°45' N, 111°8' W, 1350 m above sea level). The soil type was a Nibley silty clay loam series (fine, mixed, mesic Aquic Argiustolls).
Plots, consisting of six drilled rows 15 cm apart and 15 m long, were planted perpendicular to and on both sides of a line-source irrigation pipe using a cone seeder. The seeding rate was approximately 135 seeds per linear m of row. Alleyways (1-m wide) were mowed parallel to the line source at 3-m intervals leaving five 1- by 2-m plots, each representing a different water level (WL). Segments nearest to the line source were designated as WL-1 and the most distant plots as WL-5. Plots were arranged in a modified split-plot design with four replications, two on each side of the line source. The 10 cultivars were treated as whole plots and five WL as subplots. However, because of design limitations associated with the line-source sprinkler system, water levels were not randomized within each cultivar.
Plots were irrigated uniformly as needed during the establishment year (1995), and 56 kg N ha-1 was applied in midsummer and again in the fall. Amounts of water received by the plots from the irrigation treatment plus natural precipitation were measured with rain gauges from June until the final harvest in 1996 and from the first harvest until the final harvest in 1997 and 1998. These amounts for WL-1 through WL-5 respectively, were 538, 434, 315, 251, and 81 mm in 1996; 886, 766, 611, 525, and 373 mm in 1997; and 817, 702, 570, 499, and 350 mm in 1998. Plots were harvested with a sickle-bar mower to an 8-cm stubble at the boot stage of plant development at the first harvest and when the height of the regrowth was 25 to 30 cm at subsequent harvests. Six harvests in 1996 and 1997 and five in 1998 were made from mid-May until late September (1997) and early October (1996 and 1998). Because a plant growth gradient was not yet established across WL in 1996, only results from 1997 and 1998 are reported. Fertilizer (56 kg N ha-1) was applied prior to the first harvest and after Harvests 2, 4, and 6 in 1996 and 1997; and prior to the first harvest and after Harvests 2, 4, and 5 in 1998. Forage samples were taken from each plot and dried to a constant weight in a forced-air oven at 70°C to determine dry matter percentage. Forage yields were reported as megagrams of dry matter per hectare (DMY).
Dry matter yield was analyzed within and across years as a modified split-plot by the GLM procedure (SAS Institute Inc., 1994). Because WL were not randomized within cultivars (C), a valid test for the main effect due to WL was not available. The WL x C interaction was tested with the replication (R) x WL x C interaction. Data from individual years were treated as repeated measures in the analyses combined across years. Mean separations were made on the basis of the Fisher's protected least significant difference (LSD) at the 0.05 level of probability. Linear, quadratic, and cubic trends of DMY across WL were determined for each cultivar using orthogonal polynomials with unequal intervals (Gomez and Gomez, 1984, p. 230). Amount of water received at each WL was used in the computation of the coefficients.
Stability parameters were determined by regressing the cultivar means for specific environments, i.e., cultivar x WL x year means, on the corresponding environmental means, i.e., WL x year means (Eberhart and Russell, 1966). Computations of the environmental means did not include the value for the cultivar involved in its respective regression analysis.
| RESULTS AND DISCUSSION |
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Both linear and quadratic trends were significant in the analysis of data with and without Harvests 1, 2, and 3 (Tables 2 and 3). However, linear trends were more predominant in the latter. The linear sums of squares ranged from 93% of the WL sums of squares for MO HD-II and Alta to 77% for Forager, 81% for MO-96, and 82% for Martin when the early-season data were not included in the analyses. The quadratic response of the latter three entries was associated with a relatively stable forage yield across the first three WL followed by a relatively sharp decline thereafter (Fig. 2) .
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When all harvests were considered, Martin, Forager, Fawn, Ky 31 E+, and Alta all had relatively high annual DMY (Table 2), although the stability (b) of these cultivars across environments varied substantially. For example, the b value and standard deviation were 0.91 and 0.21 for Martin and 0.85 and 0.15 for Fawn. The b values for Alta and Forager were 1.21 and 1.17, respectively. Trends in DMY for Ky 31 E+ approached Eberhart and Russell's definition of a stable cultivar with a b value of 0.98, and a standard deviation of 0.10.
In analyses of data excluding the first three harvests, not only were the trends across WL much more pronounced, but the b values of most cultivars were closer to 1.0 and the standard deviations much smaller than in the analyses comprising all harvests (Table 3). With this scenario, selection on the basis of DMY would be a reasonable approach. It should be noted that DMY of Martin was consistently high across WL in both sets of data (Fig. 2).
Dry matter yield of Ky 31 E+ was consistently higher than Ky 31 E- in the analyses of data with and without the first three harvests (Fig. 3) . Differences were significant (P < 0.01) at WL-5 for annual DMY and at WL-4 in the analysis without the first three harvests. In the latter analysis, the difference between the two entries approached significance (P = 0.057) at WL-5. Although this relationship needs additional study, our results suggest that the presence of the Neotyphodium endophyte may have a beneficial effect on the productivity of tall fescue in the Intermountain Region, particularly as water becomes limiting.
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| CONCLUSIONS |
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Differences among cultivars were relatively consistent across WL as indicated by the generally nonsignificant cultivar x WL interactions and significant (P < 0.05 and 0.01) correlations among DMY produced at the different WL treatments. Linear and quadratic trends across WL, computed on the basis of orthogonal polynomials, were both significant; however, linear trends were much more pronounced in the analysis of data without the first three WL. Stability parameters, based on regression of cultivar means on their respective year x WL means, varied according to cultivar. When data from the first three harvests were removed, b values for most entries were close to 1.0.
The cultivar Ky 31 infected with the Neotyphodium endophyte consistently produced more DMY than its endophyte-free counterpart. Although these differences were not always significant (P < 0.05), the trends indicate that the endophytic fungus may have a positive effect on DMY of tall fescue in the Intermountain Region, particularly as water becomes limited.
On the basis of the stability indices and the relative consistency in DMY of the cultivars across WL in these studies, we conclude that annual yield averaged across levels of water stress would be a logical criterion for selecting germplasm for irrigated pastures in the Intermountain Region.
| ACKNOWLEDGMENTS |
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| NOTES |
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Received for publication March 27, 2000.
| REFERENCES |
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